Abstract
Mechanical thinning and the application of prescribed fire are commonly used to restore fire-adapted forest ecosystems in the Western United States. During a 10-year period, we monitored the effects of fuel-reduction and forest-restoration treatments on levels of tree mortality in an interior ponderosa pine, Pinus ponderosa Dougl. ex Laws., forest in California. Twelve experimental plots, ranging in size from 77–144 ha, were established to create two distinct forest structural types: mid-seral stage (low structural diversity; LoD) and late-seral stage (high structural diversity; HiD). Following harvesting, half of each plot was treated with prescribed fire (B). A total of 16,473 trees (8.7% of all trees) died during the 10-year period. Mortality was primarily attributed to bark beetles (Coleoptera: Curculionidae, Scolytinae) (10,655 trees), specifically fir engraver, Scolytus ventralis LeConte, mountain pine beetle, Dendroctonus ponderosae Hopkins, western pine beetle, D. brevicomis LeConte, pine engraver, Ips pini (Say), and, to a much lesser extent, Jeffrey pine beetle, D. jeffreyi Hopkins. Trees of all ages and size classes were killed, but mortality was concentrated in the smaller-diameter classes (19–29.2 and 29.3–39.3 cm at 1.37 m in height). Most mortality occurred three to five years following prescribed burns. Higher levels of bark beetle-caused tree mortality were observed on LoD + B (8.7%) than LoD (4.2%). The application of these and other results to the management of interior P. ponderosa forests are discussed, with an emphasis on the maintenance of large trees.
Highlights
>10 million hectares of forests are classified as having moderate- to high-fire hazards in the Western United States [1], and fuel-reduction treatments have been widely promoted to reduce the intensity and severity of future wildfires
Our goal is to address the following questions: (1) What are the effects of structural diversity and the application of prescribed fire on levels of tree mortality? (2) What are the primary causes of tree mortality and how might these vary temporally? (3) How do levels of tree mortality attributed to bark beetles vary by bark beetle species, host species, and tree size; (4) What are the potential implications to the management of interior P. ponderosa forests?
We reported that the application of prescribed fire resulted in significant increases in D. ponderosae-caused tree mortality in all but the two largest-diameter classes at Blacks
Summary
>10 million hectares of forests are classified as having moderate- to high-fire hazards in the Western United States [1], and fuel-reduction treatments have been widely promoted to reduce the intensity and severity of future wildfires Such conditions are most notable at lower elevations where short-interval, low- to moderate-intensity fire regimes predominate [2,3,4,5,6,7,8,9,10]. Frequent thinning of small-diameter (
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